| Active Filters |
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| 513256 | - 5-CL-2 - Land Converted to Cropland
- 5-SL-2 - Land Converted to Settlements
- 5-WL-1 - Wetlands Remaining Wetlands
| - 3.B.2.b.iii - Wetlands converted to Cropland
- 3.B.5.b.iv - Wetlands converted to Settlements
- 3.B.4.a - Wetlands Remaining Wetlands
| | | 1996 IPCC default | Emission factor (applicable to fuels combusted in various types of vegetation fires) | | Wetland | | | | 1554 | g/kg dry matter combusted | IPCC Good Practice Guidance for LULUCF, Table 3A.1.16, on page 3.185 | |
| 513257 | - 5-CL-2 - Land Converted to Cropland
- 5-SL-2 - Land Converted to Settlements
- 5-WL-1 - Wetlands Remaining Wetlands
| - 3.B.2.b.iii - Wetlands converted to Cropland
- 3.B.5.b.iv - Wetlands converted to Settlements
- 3.B.4.a - Wetlands Remaining Wetlands
| | | 1996 IPCC default | Emission factor (applicable to fuels combusted in various types of vegetation fires) | | Wetland | | | | 58 | g/kg dry matter combusted | IPCC Good Practice Guidance for LULUCF, Table 3A.1.16, on page 3.185 | |
| 513258 | - 5-CL-2 - Land Converted to Cropland
- 5-SL-2 - Land Converted to Settlements
- 5-WL-1 - Wetlands Remaining Wetlands
| - 3.B.2.b.iii - Wetlands converted to Cropland
- 3.B.5.b.iv - Wetlands converted to Settlements
- 3.B.4.a - Wetlands Remaining Wetlands
| | | 1996 IPCC default | Emission factor (applicable to fuels combusted in various types of vegetation fires) | | Wetland | | | | 2 | g/kg dry matter combusted | IPCC Good Practice Guidance for LULUCF, Table 3A.1.16, on page 3.185 | |
| 513259 | - 5-CL-2 - Land Converted to Cropland
- 5-SL-2 - Land Converted to Settlements
- 5-WL-1 - Wetlands Remaining Wetlands
| - 3.B.2.b.iii - Wetlands converted to Cropland
- 3.B.5.b.iv - Wetlands converted to Settlements
- 3.B.4.a - Wetlands Remaining Wetlands
| | | 1996 IPCC default | Emission factor (applicable to fuels combusted in various types of vegetation fires) | | Wetland | | | | 4 | g/kg dry matter combusted | IPCC Good Practice Guidance for LULUCF, Table 3A.1.16, on page 3.185 | |
| 513260 | - 5-CL-2 - Land Converted to Cropland
- 5-SL-2 - Land Converted to Settlements
- 5-WL-1 - Wetlands Remaining Wetlands
| - 3.B.2.b.iii - Wetlands converted to Cropland
- 3.B.5.b.iv - Wetlands converted to Settlements
- 3.B.4.a - Wetlands Remaining Wetlands
| | | 1996 IPCC default | Emission factor (applicable to fuels combusted in various types of vegetation fires) | | Wetland | | | | 0.11 | g/kg dry matter combusted | IPCC Good Practice Guidance for LULUCF, Table 3A.1.16, on page 3.185 | |
| 522676 | | - 3.B.2.b.iii - Wetlands converted to Cropland
| | | Modeled | Emissions factor representing carbon removals (CO2-C emissions) from tropical peatland soils drained for tree plantations on an annual area basis. | Peatland drainage depth | Tropical peatlands converted to or remaining as drained perennial tree crop plantations (i.e., oil palm). Initial land use could be natural forest or any other land use type. Groundwater measurements rather than field drain water table measurements. Annual mean water table depths 30-50 cm. | Tropical Southeast Asia - measurements from Indonesia (Jambi, Riau) and Malaysia (Johor, Sarawak). Mean annual precipitation 2500-3500 mm. | | EF = 5.4 + 0.21*WT (EF = total carbon loss in tonnes CO2-C/ha/yr, WT = water table depth in cm) | 13.8 | tonnes CO2-C/ha/yr | Peer-reviewed journal | |
| 522677 | | - 3.B.2.b.iii - Wetlands converted to Cropland
| | | Modeled | Emissions factor representing carbon removals (CO2-C emissions) from tropical peatland soils drained for tree plantations on an annual area basis. | Peatland drainage depth | Tropical peatlands converted to or remaining as drained perennial tree crop plantations (i.e., oil palm). Initial land use could be natural forest or any other land use type. Groundwater measurements rather than field drain water table measurements. Annual mean water table depths 50-70 cm. | Tropical Southeast Asia - measurements from Indonesia (Jambi, Riau) and Malaysia (Johor, Sarawak). Mean annual precipitation 2500-3500 mm. | | EF = 5.4 + 0.21*WT (EF = total carbon loss in tonnes CO2-C/ha/yr, WT = water table depth in cm) | 18.09272 | tonnes CO2-C/ha/yr | Peer-reviewed journal | |
| 522678 | | - 3.B.2.b.iii - Wetlands converted to Cropland
| | | Modeled | Emissions factor representing carbon removals (CO2-C emissions) from tropical peatland soils drained for tree plantations on an annual area basis. | Peatland drainage depth | Tropical peatlands converted to or remaining as drained perennial tree crop plantations (i.e., oil palm). Initial land use could be natural forest or any other land use type. Groundwater measurements rather than field drain water table measurements. Annual mean water table depths 70-90 cm. | Tropical Southeast Asia - measurements from Indonesia (Jambi, Riau) and Malaysia (Johor, Sarawak). Mean annual precipitation 2500-3500 mm. | | EF = 5.4 + 0.21*WT (EF = total carbon loss in tonnes CO2-C/ha/yr, WT = water table depth in cm) | 22.33736 | tonnes CO2-C/ha/yr | Peer-reviewed journal | |
| 522679 | | - 3.B.2.b.iii - Wetlands converted to Cropland
| | | Modeled | Emissions factor representing carbon removals (CO2-C emissions) from tropical peatland soils drained for tree plantations on an annual area basis. | Peatland drainage depth | Tropical peatlands converted to or remaining as drained perennial tree crop plantations (i.e., oil palm). Initial land use could be natural forest or any other land use type. Groundwater measurements rather than field drain water table measurements. Annual mean water table depths 90-110 cm. | Tropical Southeast Asia - measurements from Indonesia (Jambi, Riau) and Malaysia (Johor, Sarawak). Mean annual precipitation 2500-3500 mm. | | EF = 5.4 + 0.21*WT (EF = total carbon loss in tonnes CO2-C/ha/yr, WT = water table depth in cm) | 26.58199 | tonnes CO2-C/ha/yr | Peer-reviewed journal | |
| 525159 | - 5-CL-2 - Land Converted to Cropland
| - 3.B.2.b.i - Forest Land converted to Cropland
- 3.B.2.b.iii - Wetlands converted to Cropland
| | | Other (e.g. compiled) | Aboveground Biomass Carbon Stock Change | From undisturbed natural mangrove to coconut plantation | Vegetation/crop type/subtype: ; Species: ; Biomass attributes/age: ; Soil type/nutrient content: . | Spatial boundaries: Philippines , Palawan; Climate: ; Ecological zone: ; Temperature: ; Moisture: . | | Time since landuse: 20 years | -25.9905896665235 | tonnes C/ha | Peer-reviewed journal | |
| 525191 | - 5-CL-2 - Land Converted to Cropland
| - 3.B.2.b.i - Forest Land converted to Cropland
- 3.B.2.b.iii - Wetlands converted to Cropland
| | | Other (e.g. compiled) | Belowground Biomass Carbon Stock Change | From undisturbed natural mangrove to coconut plantation | Vegetation/crop type/subtype: ; Species: ; Biomass attributes/age: ; Soil type/nutrient content: . | Spatial boundaries: Philippines , Palawan; Climate: ; Ecological zone: ; Temperature: ; Moisture: . | | Time since landuse: 20 years | -12.3212155908592 | tonnes C/ha | Peer-reviewed journal | |
| 525196 | - 5-CL-2 - Land Converted to Cropland
| - 3.B.2.b.i - Forest Land converted to Cropland
- 3.B.2.b.iii - Wetlands converted to Cropland
| | | Other (e.g. compiled) | Soil Carbon Stock Change | From undisturbed natural mangrove to abandoned rice field | Vegetation/crop type/subtype: ; Species: ; Biomass attributes/age: ; Soil type/nutrient content: . | Spatial boundaries: Guinea-Bissau, Cacheu; Climate: ; Ecological zone: ; Temperature: ; Moisture: . | Rice field | Time since landuse: 17.5 years. Soil depth: 80 | -95.48 | tonnes C/ha | Peer-reviewed journal | |
| 525197 | - 5-CL-2 - Land Converted to Cropland
| - 3.B.2.b.i - Forest Land converted to Cropland
- 3.B.2.b.iii - Wetlands converted to Cropland
| | | Other (e.g. compiled) | Soil Carbon Stock Change | From undisturbed natural mangrove to abandoned rice field | Vegetation/crop type/subtype: ; Species: ; Biomass attributes/age: ; Soil type/nutrient content: . | Spatial boundaries: Guinea-Bissau, Oio; Climate: ; Ecological zone: ; Temperature: ; Moisture: . | Rice field | Time since landuse: 17.5 years. Soil depth: 80 | -37 | tonnes C/ha | Peer-reviewed journal | |